Designation C 970 – 87 (Reapproved 2006) Standard Practice for Sampling Special Nuclear Materials in Multi Container Lots1 This standard is issued under the fixed designation C 970; the number immedia[.]
Trang 1Designation: C 970 – 87 (Reapproved 2006)
Standard Practice for
Sampling Special Nuclear Materials in Multi-Container
This standard is issued under the fixed designation C 970; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision A number in parentheses indicates the year of last reapproval A
superscript epsilon (e) indicates an editorial change since the last revision or reapproval.
1 Scope
1.1 This practice provides an aid in designing a sampling
and analysis plan for the purpose of minimizing random error
in the measurement of the amount of nuclear material in a lot
consisting of several containers The problem addressed is the
selection of the number of containers to be sampled, the
number of samples to be taken from each sampled container,
and the number of aliquot analyses to be performed on each
sample
1.2 This practice provides examples for application as well
as the necessary development for understanding the statistics
involved The uniqueness of most situations does not allow
presentation of step-by-step procedures for designing sampling
plans It is recommended that a statistician experienced in
materials sampling be consulted when developing such plans
1.3 The values stated in SI units are to be regarded as the
standard
1.4 This standard does not purport to address all of the
safety problems, if any, associated with its use It is the
responsibility of the user of this standard to establish
appro-priate safety and health practices and determine the
applica-bility of regulatory limitations prior to use.
2 Referenced Documents
2.1 ASTM Standards:2
E 300 Practice for Sampling Industrial Chemicals
2.2 Other Standard:
NUREG/CR-0087, Considerations for Sampling Nuclear
Materials for SNM Accounting Measurements3
3 Terminology Definitions
3.1 analysis of variance—the body of statistical theory,
methods, and practice in which the variation in a set of
measurements, as measured by the sum of squares of the measurements, is partitioned into several component sums of squares, each attributable to some meaningful cause (source of variation)
3.2 confidence interval—(a) an interval estimator used to
bound the value of a population parameter and to which a
measure of confidence can be associated, and (b) the interval
estimate, based on a realization of a sample drawn from the
population of interest, that bounds the value of a population parameter [with at least a stated confidence]
3.3 Estimation, Estimator, Estimate:
3.3.1 Estimation, in statistics, has a specific meaning,
con-siderably different from the common interpretation of guess-ing, playing a hunch, or grabbing out of the air Instead, estimation is the process of following certain statistical prin-ciples to derive an approximation (estimate) to the unknown value of a population parameter This estimate is based on the information available in a sample drawn from the population
3.4 estimator—a function of a sample (X 1 , X 2 , , X n) used
to estimate a population parameter
N OTE 1—An estimator is a random variable; therefore, not every
realization (x 1 , x 2 , , x n ) of the sample (X 1 , X 2 , , X n) will lead to the same value (realization) of the estimator An estimator can be a function that, when evaluated, results in a single value or results in an interval or
region of values In the former case the estimator is called a point estimator, and in the latter case it is referred to as an interval estimator.
3.5 estimate, (a: n)—a particular value or values realized by
applying an estimator to a particular realization of a sample,
that is, to a particular set of sample values (x 1 , x 2 , , x n ) (b:
v)—to use an estimator.
3.6 nested design— one of a particular class of experimental
designs, characterized by “nesting” of the sources of variation:
for each sampled value of a variable A, a given number of values of a second variable B is sampled; for each of these, a given number of values of the next variable C is sampled, etc.
The result is that each line of the “Expected Value of Mean Square” column in an analysis of variance table contains all but one of the terms of the preceding line
3.7 random variable— a variable that takes on any one of
the values in its range according to a [fixed] probability distribution (Synonyms: chance variable, stochastic variable, variate.)
1
This practice is under the jurisdiction of ASTM Committee C26 on Nuclear
Fuel Cycle and is the direct responsibility of Subcommittee C26.08 on Quality
Assurance and Reference Materials.
Current edition approved Jan 1, 2006 Published February 2006 Originally
approved in 1982 Last previous edition approved in 1997 as C 970 – 87 (1997).
2 For referenced ASTM standards, visit the ASTM website, www.astm.org, or
contact ASTM Customer Service at service@astm.org For Annual Book of ASTM
Standards volume information, refer to the standard’s Document Summary page on
the ASTM website.
3
Available from National Technical Information Service, Springfield, VA 22161.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
Trang 23.8 standard deviation (s.d.)—the positive square root of the
variance
3.9 variance—(a: population) the expected value of the
square of the difference between a random variable and its own
expected value; that is, the second moment about the mean (b:
sample) The sum of squared deviations from the sample mean
divided by one less than the number of values involved
4 Significance and Use
4.1 Plans for sampling and analysis of nuclear material are
designed with two purposes in mind: the first is related to
material accountability and the second to material
specifica-tions
4.2 For the accounting of special nuclear material, sampling
and analysis plans should be established to determine the
quantity of special nuclear material held in inventory, shipped
between buyers and sellers, or discarded Likewise, material
specification requires the determination of the quantity of
nuclear material present Inevitably there is uncertainty
asso-ciated with such measurements This practice presents a tool
for developing sampling plans that control the random error
component of this uncertainty
4.3 Precision and accuracy statements are highly desirable,
if not required, to qualify measurement methods This practice
relates to“ precision” that is generally a statement on the
random error component of uncertainty
5 Designing the Sampling Plan—Measuring Random
Error
5.1 The random error component of measurement
uncer-tainty is due to the various random errors involved in each
operation such as weighing, sampling, and analysis The
quantification of the random error is usually given in terms of
the variance of the mean of the measurements When analyzing
a lot of nuclear material to estimate the true concentration, p,
of a constituent such as uranium, the sample mean, p¯, is the
calculated estimator The variance of p¯, s p ¯2, is a measure of
the random error associated with the measurement process
This practice deals primarily with random error; measurement
process systematic error will be discussed briefly in8.2
5.2 To estimate the true concentration, p, in a lot consisting
of N containers using a completely balanced nested design,
randomly select n of the N containers; from each of the n
containers, randomly select m samples; perform r laboratory
analyses on each of the nm samples (It is assumed that the
amount of material withdrawn for samples is only a small
fraction of the total quantity of material.) Let
X ijk 5 measured concentration of the constituent in the k th analysis
on the jth sample from the i th container, or
where:
p = true concentration,
b i = effect due to container i,
s ij = effect due to the j th sample from container i, and
a ijk = effect due to the k th analysis on the j thsample from
container i.
Then, if each container holds the same amount of material,
(Note 2), the sample mean
p¯ 5 X ¯ 5 1
nmr (
i 5 1
n
(
j 5 1
m
(
k 5 1
r
is an estimator of the true value p The true variance of p¯ is
then
sp¯ 5sb
n
~N 2 n!
N 2 1 1
ss2
nm1
sa
where:
sb = true variance among the N containers in the
given lot, defined as N −1 (p i 2 − N −2 ((p i ) 2;
ss 2 = true variance among samples taken from a
single container,
sa 2 = true variance of the laboratory analysis on
a homogeneous sample, and
N 2 n
N 2 1
= finite population correction factor
N OTE 2—If the ith container has g igrams of material, then the true average concentration is (1N
w ip i , where w i = g i/(1N
gi However, the
variance of the corresponding estimate can still be calculated as shown in
this guideline; the true variance will be only slightly larger if the g ivalues
do not differ too much For example, if the s.d of the g iwere 20 % of the
average g i , it can be shown that the s.d of p would be underestimated by about 2 % of the true standard deviation; for g i’s having s.d.’s of 10 % or
30 % of their average, the underestimation is 0.5 % or 4.5 % respectively.
Note that a set of 25 weights g i, uniformly spread from 3.3 to 6.7 kg, has
a s.d equal to 20 % of the average (5 kg) (It is assumed that errors in the estimation of net weights are insignificant compared to differences between containers, sampling variability, and analytical uncertainty, or both.)
5.3 Since the true variances sb, ss2, and sa are generally unknown, they may be estimated using appropriate data Those data can be historical data obtained from analyzing production samples, as long as there have been no changes in the process with time If such data are not available, as for example during the start-up of a facility or after a change in process conditions,
a designed experiment is required to obtain estimates of the variances.4
5.4 An estimate s p ¯2of the variance of the sample mean can
be obtained from Eq 3, by inserting estimates of the variances appearing there If a designed experiment is performed, the estimates can be obtained from the mean squares
It is shown inAppendix X1 that estimates of the variances are as follows:
s s25 1
r ~MS s 2 MS a!, (5)
s b 5N 2 1 Nmr ~MS b 2 MS s!, (6)
where:
MS a, MSb , and MS s are the “mean squares” for analyses,
4
This topic can be found in many standard statistical texts, for example,
Brownlee, K A., Statistical Theory and Methodology in Science and Engineering,
2nd ed., John Wiley and Sons, New York, 1965; Bennett, C A., and Franklin, N L.,
Statistical Analysis in Chemistry and the Chemical Industry, John Wiley and Sons,
New York, 1954; Mendenhall, William, Introduction to Linear Models and the
Design and Analysis of Experiments, Duxbury Press, Belmont, CA, 1968; and in
Jaech, J L., “Statistical Methods in Nuclear Material Control,” (TID-26298, USAEC, 1973).
Trang 3containers and samples The estimated variance of p¯ is
ob-tained by replacing the true variances in Eq 3 by their
estimates:
s ¯ p25 1
n
N 2 n
N 2 1 s b 1 1
nm s s
2 1 1
nmr s a (7)
Finally, expressed in terms of the mean squares, this
be-comes
s p¯ 5 1
nmr
N 2 n
N MS b1 1
Nmr MS s. (8)
5.5 The variance of the sample mean, sp ¯2, or its estimate, s
p ¯2, is used to calculate confidence limits for the quantity and
concentration of nuclear materials Therefore, it is desirable to
reduce this variance and, in this way, reduce the random error
Obviously, this can be done by using large values of n, m, and
r (large number of samples and laboratory analyses) The cost
and time required by that approach could be prohibitive
Another approach is to improve the overall process such that
the basic variances sb2, ss2, sa2are reduced
5.6 Eq 8 gives an estimate of the variancesp ¯2for any given
n, m, and r and therefore can be used for comparing different
sampling plans An example of two sampling plans involving
the same number of analyses but having different random
errors is given inAppendix X3
5.7 When one has fixed resources within which the
sam-pling plan must function, the question arises as how to allocate
these resources to obtain the “best” sampling plan Sections6
and7discuss this problem when “cost” is considered “Cost”
is used generically here—it need not be a monetary quantity; it
could be time or something else
6 Determining Sample Sizes
6.1 There are two common situations in which sampling
plans must be developed for use in nuclear material
measure-ment when there are constraints on resources In the first
situation a constraint is imposed upon the “cost” of sampling
and analysis In this case, the problem is to find a plan that
minimizes the variance of the sample mean (minimizes random
error) subject to the cost constraint In the second situation, a
constraint is imposed upon the variance of the sample mean
(upon the random error) and the problem is to find a plan which
minimizes cost subject to this constraint Since this latter
problem is the most frequently encountered, methods for its
solution will be given The former problem, for which the
solution technique closely parallels the one given, will be
covered in footnotes
6.2 Component Variances Are Known:
6.2.1 If the variance constraint is expressed as a maximum
value for the width, 2D, of a confidence interval for p, it can be
transformed immediately to a maximum value for sp ¯, by using
the relationship
D 5 ~Z12a/2!s¯ p
(9)
where:
Z 1-a/2 = value having a probability a/2 of being exceeded by a
standard normal variate
Therefore, if D is limited to Do, say, then sp ¯is limited to Do/
Z 1−a/2 Since the minimum cost is achieved when the constraint
is barely satisfied, we need to minimize cost subject to the constraint
where K is a constant, either specified directly or computed
from Doand a
6.2.2 When the underlying variances are known from pre-vious history, the problem of achieving a minimum cost within
a stated confidence interval width reduces to finding a suitable
set of values for n, m, and r InAppendix X2it is shown that
the optimum r and m are given by
r 5ssa
sSc s
c aD1 / 2
(11)
m 5sss
bSc b
c s
N 2 1
N D1 / 2
(12)
where:
c b = marginal cost of choosing one additional container and preparing it for sampling,
c s = marginal cost of drawing an additional sample from a container and preparing it for analysis, and
c a = marginal cost of an additional laboratory analysis
Therefore, the optimum values for r and m do not depend on
n, and in fact can be calculated immediately from the
vari-ances, the “costs,” and N.
6.2.3 Once m and r are determined and inserted into Eq 3, s
p ¯2is seen to be a monotonic decreasing function of n, so that one need only make n large enough to achieve the required
bound on s p ¯2(Note 3) Letting c s= ca= cb= 1.0 provides the
optimum values of r, m, and n when costs are considered equal.
In practice, the optimum values for m and r obtained this way
are unlikely to be integers Unless these values are very close
to integers, it is prudent to consider both bracketing values, that
is, if the optimum value for r is1.4, try both r = 1 and r = 2 The reason is that the final value of n will generally be different and it is not clear beforehand which set of values of r, m, and
n will achieve the required variance at minimum cost It is also
possible to use different values of m (or r, or both) for different
containers or samples, or both, to obtain a non-integer
“effec-tive” value of m (or r, or both) In this case, p¯ should be
replaced by a weighted average; s p ¯2becomes more compli-cated; and the expected values of the mean squares also become more complicated, as does the estimate of s p ¯2 The advice of a statistician is strongly suggested if this approach is being considered
N OTE 3—The same values of m and r provide minimum variance for
given cost When these are inserted into the cost function, it is seen to be
proportional to n, so that n should be chosen as large as the cost constraint
will allow.
6.2.4 An example with further discussion is given in Ap-pendix X3
6.3 Component Variances Are Not Known:
6.3.1 The approach to finding values for n, m, and r
described in Appendix X2 is also valid when the basic variances are not known, provided some estimates of these variances are available As in 6.2, values for m and r can be
C 970 – 87 (2006)
Trang 4obtained from estimates of the variances and cost factors.
There is a complication in the calculation of an optimum value
of n, however: since the final uncertainty will be based not on
the true variances but rather on estimates, the t-distribution4
must be used instead of the Normal Given the allowable
half-width D, we have
where:
t1−a/2(n) = value having probability a/2 of being exceeded by a
“Student’s t” variable with degrees of freedom n, and s
p ¯= estimated standard deviation of the mean
Unfortunately, n depends upon n, m, and r (and if prior data are
to be combined with present data in computing s p ¯it depends
also upon the degrees of freedom appropriate to those data)
We therefore proceed iteratively We guess n, calculate n (as
described in6.3.2), obtain t from standard tables, and calculate
s p ¯from Eq 13 We then use this target value and our estimates
of the basic variances to obtain an optimum value for n as in
6.2.3 If this optimum value is as large as, but not too much
larger than, the guessed value, it should be used Otherwise,
use it in place of the initial guess and repeat the procedure
6.3.2 The uncertainty in the final p¯ will be expressed in
terms of an estimated variance s p ¯2 The t-factor used with s p ¯
in Eq 13 has been shown to be approximately correct, provided
the degrees of freedom parameter, n, is properly chosen
Satterthwaite’s formula is applicable, whether or not the data
from a prior experiment are to be used In the simple case
where only the n 3 m 3 r data values under consideration are
used, the formula5is
n 5 s ¯ p4F N 2 n
nmrND2
MS b
n 2 11S 1
mrND2
MS s2
n~m 2 1!G21
(14)
When prior data are combined with these data, the formula
is more complicated
6.3.3 When n and m are both greater than one, the approach
given here leads to an unbiased estimate of sp ¯2 If n or m, or
both, are chosen to be one, then the corresponding mean
square(s) (Appendix X1) are undefined If n = 1, no estimate of
sp ¯2is available If n > 1 and m = 1, then only an overestimate
of s p ¯ 2is available: (1/nmr) MS b has expected value (s b2/n)
(N/(N − 1)) + (s s2/nm) + (s a2/nmr), in which the first term is
too big by the factor (N/(N − 1)) Therefore, in order to avoid
this problem, it is desirable to choose n greater than one; and
unless N is large, also choose m greater than one.
7 Compositing Samples
7.1 In the example ofAppendix X3 at least seven samples
and seven laboratory analyses (measurements) were needed to
reduce the variance of the sample mean to the specified value
Laboratory measurements are usually costly and time
consum-ing Sampling operations, on the other hand, are relatively
inexpensive from the viewpoint of required instrumentation
and operator time Furthermore, in many SNM accountability
situations the variance components due to between- and
within-container variabilities are not known with the same degree of confidence as the laboratory variance To reduce the effort in the laboratory and to minimize the random error, it could be desirable to blend samples to form a composite
7.2 When each container in a lot (n = N) is sampled m times with r analyses per sample, the finite population correction
factor in Eq 3 becomes zero and Eq 3 becomes:
sp¯ 5 1
N Sss2
m 1
sa
mrD5 1
Nm Sss21sa
r D (15)
If the m samples from each individual container are
com-posited and thoroughly mixed (Note 4) and each of the N composites is analyzed r times, Eq 15 is replaced by:
sp¯ 5 1
NSss2
m 1
sa
The laboratory effort is still rather large, since even for r = 1
a total of Nr = N measurements must be made.
N OTE 4—Thorough mixing is very important to give effective homog-enizing of the composite samples, thereby reducing the error from subsampling to a negligibly small value.
7.3 To further reduce the laboratory effort, the m samples from each of the N containers in the lot may be composited into
a lot master sample and thoroughly mixed The contributions to
the master sample from each of the N containers should be
proportional to the net weights in the corresponding containers
A sub-sample (Note 5) of the composite is then analyzed r
times The variance of the sample mean is given by
sp¯ 5ss
2
Nm1
sa
N OTE 5—Dissolution of the material is a step in the laboratory analysis; therefore, the sub-sample must contain an amount of material sufficient for
further subdivision into r portions.
7.4 For this latter case, it is shown inAppendix X4that the
values of m and r that minimize “cost” for a given variance bound k are
m 5sN sS=c asa1=c sss
r 5 s aS=c asa1=c sss
Finally, the minimum cost is given by
minimum cost 51
k ~=c asa1=c sss!2 (20)
(Note 6)
Note that, while Eq 18 and Eq 19 give m and r, the values
will not generally be integers If the values are rounded to integers, then Eq 20 is not appropriate for calculating the actual
cost corresponding to the chosen m and r Instead, the cost would be calculated as c s Nm + c a r.
N OTE 6—If it is desired to minimize the variance for given cost C, the
same technique leads to
mN=c s
r=c a
sa 5
C
=c sss1=c asa , and (21)
5Mendenhall (op cit), p 352; also Jaech (op cit), pp 157–161.
Trang 5the minimum variance is given by
minimum variance 5C1 ~=c asa1=c sss!2 (22)
7.5 An example with further discussion is given in
Appen-dix X5
7.6 Compositing in this way has a major drawback, in that
it is impossible to estimate ss2, the within-container variance,
on a continuing basis Quite possibly ss 22 may change,
especially if there has been a change in process conditions or
supplier Periodically, and especially at those times when a
change in ss 2might be expected, a number of samples may be
drawn from each container and analyzed separately in replicate
to establish current estimates of ss2and sa
8 Mechanical and Physical Aspects of Sampling
8.1 The common types of nuclear material encountered are
liquid and solids (powder and pellets) In whatever form
encountered, the principal task in sampling is to remove a
sample that is typical of the bulk material, at least as far as the
parameters of interest are concerned The selection of a
procedure and equipment for sampling must be made based on
factors such as the following:
8.1.1 Type and form of the material,
8.1.2 Degree of homogeneity,
8.1.3 Stability of the material,
8.1.4 Location of the material,
8.1.5 Purpose and requirements for analyzing the material,
and
8.1.6 Accessibility for sampling all units or containers
involved
8.1.7 Practice E 300 and NUREG/CR-0087 present
prin-ciples and guidelines for sampling materials The mechanical
and physical aspects of sampling are discussed
NUREG/CR-0087 addresses sampling nuclear materials to determine their chemical and isotopic contents
8.2 Some Sources of Error:
8.2.1 There are various sources of error in the sampling process such as nonhomogeneity, contamination of the sample after removal from the bulk material, failure of the equipment, failure of the operator to follow the procedure, bias, and chemical and physical changes in the material during sampling The latter two sources of error are discussed briefly in8.2.2and 8.2.3
8.2.2 Bias occurs when, in addition to the random errors, all measured values are shifted consistently from the true value in the same direction Likely sources of bias are improper sampling procedures, faulty sampling devices, and improperly calibrated instruments The problem is to detect the existence
of such biases and to account for them in the results The solution to this problem usually requires designing an appro-priate study.6This may not always be possible For example, if the sample were contaminated to an unknown degree and new samples are not available, it may be impossible to estimate the bias
8.2.3 An example of errors due to chemical or physical changes occurs with plutonium dioxide powder.7This material, which is usually handled as a fine powder with a large surface area, readily picks up or loses water if exposed to a change in humidity Plutonium dioxide powder can gain over 1 % in weight within a few hours if exposed to an increase in humidity Therefore, very careful control over conditions must
be established and maintained when sampling this material, particularly if it is relocated and then sampled
APPENDIXES (Nonmandatory Information) X1 ESTIMATION OF VARIANCES IN A NESTED ANALYSIS OF VARIANCE DESIGN
X1.1 Let X ijk be the kth measurement on the jth sample
from the ith container, k = 1, , r; j = 1, , m; i = 1, , n.
Let
X ij.5 (
k 5 1
r
X ijk , X ¯ ij.5 1
X i 5 (
j 5 1
m
(
k 5 1
r
X ijk , X ¯ i 5 1
mr X i , and (X1.2)
X 5 (
i 5 1
n
(
j 5 1
m
(
k 5 1
r
X ijk , X ¯ 5 1
X1.1.1 Then the mean squares may appear in a nested analysis of variance (ANOVA) table as follows:
Source Mean Square Expected Value of
Mean Square Containers MS b = [mr/(n − 1)]
· ((n
i = 1 (X ¯ i − X ¯ )2
[mrN/(N − 1)]s b
+ rs s
2
+ sa
Expected Value of Mean Square Samples MS s = [r/n(m − 1)]
·(n
i = 1(m
j = 1 (X ¯ ij. − X ¯ i )2
rs s2+ sa
Analyses MS a = [1/nm(r − 1)]
·(n
i = 1(m
j = 1(r
k = 1 (X ijk − X ¯ ij.) 2
sa
6
Stephens, F B., et al, Methods for the Accountability of Uranium Dioxide,
NUREG-75/010, pp 1–17, U S Nuclear Regulatory Commission, National Technical Information Service, Springfield, VA, 1975.
7Gutmacher, R G., et al, Methods for the Accountability of Plutonium Dioxide,
USAEC Report WASH-1335, 1974.
C 970 – 87 (2006)
Trang 6Note that factor [(N/(N − 1)] is due to the finite number of
containers From the preceding table, it is seen that estimates of
the variances are as follows:
s s25 1
s b 5N 2 1
X1.1.2 In practice the latter two estimates could be negative which would require modification of this estimation procedure.4
X2 FINDING THE OPTIMAL VALUES OF r AND m FOR MINIMIZING “COST” SUBJECT TO THE
CONSTRAINT THAT s p¯2 = K (see6.2 )
X2.1 The total cost8of sampling and analysis is not linear
(in n, m, and r) over the whole range of these variables.
However, in the neighborhood of the optimum, a linear
approximation is likely to be reasonable Write the variable
part of the cost as
c 5 c b n 1 c s m8 1 c a r8 (X2.1)
where:
m8 = mn,
r8 = nmr and, as in6.2.2,
c b = marginal cost of choosing one additional container
and preparing it for sampling,
c s = marginal cost of drawing an additional sample from a
container and preparing it for analysis, and
c a = marginal cost of an additional laboratory analysis
Then applying the Lagrange multiplier technique,9we
con-sider the expression
L 5 C 1 l~s p¯ 2 K!, (X2.2)
where (see Eq 3, S 5.2 ):
sp¯ 5 sb
n ·
N 2 n
N 2 11
ss2
m8 1
sa
Taking partial derivatives with respect to r8, m8, n, and l,
setting them equal to zero, and solving for l gives
l 5 c a
sa r825 c s
ss2m825c b
sb
N 2 1
N n
2
(X2.4)
From this it follows that the optimum r and m are given by
r 5 m8 r8 5ssa
sSc s
c aD1 / 2
m 5 m8 n 5ss
sbSc b
c s
N 2 1
N D1 / 2
(X2.6)
X3 EXAMPLE
X3.1 Find values of n, m, and r that meet a variance
constraint and minimize “cost” (6.2.4) Let N = 20; s b= 0.3;
ss= 0.1; and s a = 0.04 For a = 0.05, Z 1−a/2= 1.96 and if
D= 0.2, the target value for sp ¯2is given by:
K 5 D2/Z12a/2 5 0.22
From Eq 3 in X2, r 5 0.040.1 c s
1/2
c a ,
which is close to 1 whenever 5 <cs⁄ca< 10 Since the cost of
sampling is unlikely to be more than ten times the cost of an
analysis and since r $ 1, r will usually be taken equal to one.
Likewise, m 5 0.10.3~c b/c s 3 19/20!1/2 , which is close
to 1 whenever 8 <cb⁄cs< 15 Since m $ 1, m will usually be
taken to be one With r = m = 1,
sp¯ 5 0.09
n
20 2 n
0.01
n 1
0.0016
5 0.10633
setting sp ¯2= 0.0104, we obtain n = 7.03.
Thus the required variance is (approximately) achieved by
taking n = 7, m = r = 1.
X3.2 The previous paragraph shows that at least 7 contain-ers out of the 20 must be selected, sampled once, and each sample analyzed once to obtain the target value of 0.0104 for
sp ¯2and therefore meet the specified confidence interval width (2D) of 0.4 The seven containers must be selected at random, that is, each of the 20 containers is assigned one of a sequence
of numbers and a random number table is used to select the seven containers
X3.3 Note that in this case, the variance term involving
variance bound of 0.0104, unless n $ 7; and the other terms contribute so little that for n = 7, the total variance is down to the required value even for m = r = 1 Therefore, (a) we need
n $ 7 and (b) once n = 7, m and r do not need to be any larger
than their minimum value, so these optimum values are really independent of the costs This will not always be so, of course X3.4 Significant improvements in the variance s p ¯ 2 can
8 Cost need not be monetary.
9
Mendenhall, op cit, p 355.
Trang 7sometimes be achieved with small additional cost by
judi-ciously choosing values for n, m,and r This is apparent by
comparing the sets: n = 7, m = 2, r = 1 and n = 14, m = 1,
r = 1 In both situations 14 sampling operations and 14
analyses are required, that is, the total effort is about equal
However, for the second set ( n = 14), the variance is 0.0029, which is lower by a factor of three than for the first set (n = 7), which has a variance of 0.0096 Therefore, the set with n = 14
is preferred, unless the cost of choosing additional containers is quite large
X4 FINDING THE OPTIMAL VALUES FOR r AND m—COMPOSITE SAMPLE CASE (7.4)
X4.1 Selection of m and r to minimize cost for a given
variance bound K is achieved by the Lagrange multiplier
technique that was used inAppendix X2 The function to be
considered is
L 5 c s Nm 1 c a r 1 lSss2
Nm1
sa
Setting the partial derivatives with respect to m and r equal
to zero, and solving for l yields
l 5c s N2m2
ss2 5
c a r2
sa
Then, usingss2⁄Nm +sa2⁄r = K , the values for m and r can
be given in symmetric form as
mN=c s
r=c a
sa 5
=c asa1=c sss
X5 EXAMPLE
X5.1 Find values of m and r that meet a variance constraint
and minimize “cost”—composite sample case (7.5)
X5.1.1 A lot consists of N = 20 containers.
Let
ss 2 = 0.01
sa 2 = 0.0025
c s = 1 unit
c a = 16 units
X5.1.1.1 Suppose the variance of p¯ is not to exceed
k = 0.001 Then, from X4,
mN
0.15
4r
0.055
0.2 1 0.1
so that
m 5300 3 0.1
X5.1.1.2 The minimum cost is found to be 90 units If m and
r are rounded up to 2 and 4, the actual cost is, of course,
1 3 20 3 2 + 16·4 = 104 units, and the actual variance is 0.000875 If instead of compositing, one sample were taken from each container and analyzed, the cost would be 340 units, and the variance would be 0.000625
ASTM International takes no position respecting the validity of any patent rights asserted in connection with any item mentioned
in this standard Users of this standard are expressly advised that determination of the validity of any such patent rights, and the risk
of infringement of such rights, are entirely their own responsibility.
This standard is subject to revision at any time by the responsible technical committee and must be reviewed every five years and
if not revised, either reapproved or withdrawn Your comments are invited either for revision of this standard or for additional standards
and should be addressed to ASTM International Headquarters Your comments will receive careful consideration at a meeting of the
responsible technical committee, which you may attend If you feel that your comments have not received a fair hearing you should
make your views known to the ASTM Committee on Standards, at the address shown below.
This standard is copyrighted by ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959,
United States Individual reprints (single or multiple copies) of this standard may be obtained by contacting ASTM at the above
address or at 610-832-9585 (phone), 610-832-9555 (fax), or service@astm.org (e-mail); or through the ASTM website
(www.astm.org).
C 970 – 87 (2006)